[go: up one dir, main page]

CN113832042B - Salt-tolerant Saccharomycopsis fibuligera and application thereof in high-salt high-COD sewage treatment - Google Patents

Salt-tolerant Saccharomycopsis fibuligera and application thereof in high-salt high-COD sewage treatment Download PDF

Info

Publication number
CN113832042B
CN113832042B CN202111215422.7A CN202111215422A CN113832042B CN 113832042 B CN113832042 B CN 113832042B CN 202111215422 A CN202111215422 A CN 202111215422A CN 113832042 B CN113832042 B CN 113832042B
Authority
CN
China
Prior art keywords
salt
cod
tolerant
strain
application
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN202111215422.7A
Other languages
Chinese (zh)
Other versions
CN113832042A (en
Inventor
郭亭
张宿义
魏荷芬
宋珊
刘桂文
曾伟
朱杰
李�杰
张腾
颜禹
朱礼
应汉杰
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Nanjing Institute Of White Biotech Co ltd
Luzhou Pinchuang Technology Co Ltd
Luzhou Laojiao Co Ltd
Original Assignee
Nanjing Institute Of White Biotech Co ltd
Luzhou Pinchuang Technology Co Ltd
Luzhou Laojiao Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Nanjing Institute Of White Biotech Co ltd, Luzhou Pinchuang Technology Co Ltd, Luzhou Laojiao Co Ltd filed Critical Nanjing Institute Of White Biotech Co ltd
Priority to CN202111215422.7A priority Critical patent/CN113832042B/en
Publication of CN113832042A publication Critical patent/CN113832042A/en
Application granted granted Critical
Publication of CN113832042B publication Critical patent/CN113832042B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/34Biological treatment of water, waste water, or sewage characterised by the microorganisms used
    • C02F3/347Use of yeasts or fungi
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/30Organic compounds
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Microbiology (AREA)
  • Mycology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

The invention belongs to the field of environmental microorganisms, and particularly relates to a salt-tolerant ascochyta tectorial membrane yeast and application thereof in high-salt high-COD sewage treatment. For the problem of poor microbial high-salt tolerance in high-salt and high-COD sewage, the invention provides a strain of salt-tolerant saccharomyces cerevisiae (Saccharomyces fibuligera) which is preserved in Guangdong collection of microorganisms with the preservation number of GDMCC No. 61874. The invention also provides application of the salt-tolerant saccharomycete tectorial membrane yeast in high-salt and high-COD sewage treatment. The salinity tolerance range of the saccharomycete strain of the Fujianfecti provided by the invention is 0-20%, the degradation of COD can be carried out under the conditions that the NaCl content is 3-5% and the initial COD is not less than 15000mg/L, and the effluent can reach the third level of the Integrated wastewater discharge Standard GB 8978-1996.

Description

一株耐盐扣囊复膜孢酵母及其在高盐高COD污水处理中的应用A salt-tolerant yeast strain of S. forticulata and its application in the treatment of high-salt and high-COD sewage

技术领域technical field

本发明属于环境微生物领域,具体涉及一株耐盐扣囊复膜孢酵母及其在高盐高COD污水 处理中的应用。The invention belongs to the field of environmental microorganisms, and in particular relates to a strain of salt-tolerant yeast S. forticulata and its application in high-salt and high-COD sewage treatment.

背景技术Background technique

嗜盐耐盐真菌是一类能够在高盐环境下生长或者需要高盐环境才能生长的极端环境真核 微生物。长久以来,人们一直认为高盐环境下没有真菌的存在,直到1985年,Radewan等从埃及土壤中分离得到一些喜盐的真菌,经鉴定主要属于曲霉属和青霉属,这才证实了高盐 度环境下也存在真菌区系。此后,陆续有一些新的嗜盐耐盐真菌被从盐湖、晒盐场等高盐环 境或一些盐腌制食物上被分离到,例如Gunde-Cimerman等从盐场分离到几株酵母属真菌, 它们能在质量分数为3%-30%的NaCl环境下生长;李艳华从盐场分离到一株Strepospora halophile,能在5%-30%的NaCl环境下生长;Saritac从死海中分离到几株真菌,分别属于青霉属和曲霉属,它们能在20%-25%的NaCl环境下生长。但是由于嗜盐耐盐真菌生长较慢, 缺乏竞争力,所以相对于嗜盐古菌和嗜盐细菌来说,关于嗜盐耐盐真菌的报道仍然很少。嗜 盐耐盐真菌具有独特的耐盐机制,并且往往能够产生特殊的代谢产物,对于工业生产抗生素、 有机酸、工业酶制剂、改善植物抗盐抗旱和开发新型材料等有着重要意义。因此,嗜盐真菌是一类极具研究价值的微生物。Halophilic and halophilic fungi are a type of extreme environmental eukaryotic microorganisms that can grow in a high-salt environment or require a high-salt environment to grow. For a long time, people have always believed that there is no fungus in a high-salt environment. It was not until 1985 that Radewan et al. isolated some salt-loving fungi from Egyptian soil, which were mainly identified as Aspergillus and Penicillium. This confirmed the high-salt environment. There are also fungal flora in low-temperature environments. Since then, some new halophilic and halal-tolerant fungi have been isolated from high-salt environments such as salt lakes and salt fields, or some salt-cured foods. It can grow in an environment with a mass fraction of 3%-30% NaCl; Li Yanhua isolated a strain of Strepospora halophile from a salt field, which can grow in an environment of 5%-30% NaCl; Saritac isolated several strains of fungi from the Dead Sea, respectively Belonging to Penicillium and Aspergillus, they can grow in 20%-25% NaCl environment. However, because halophilic and halophilic fungi grow slowly and lack competitiveness, compared with halophilic archaea and halophilic bacteria, there are still few reports on halophilic and halophilic fungi. Halophilic and halo-tolerant fungi have a unique salt-tolerant mechanism and can often produce special metabolites, which are of great significance for industrial production of antibiotics, organic acids, industrial enzymes, improvement of plant salt and drought resistance, and development of new materials. Therefore, halophilic fungi are a class of microorganisms with great research value.

通常高盐污水是含盐的质量分数较高,>1%,有的高达10%以上,且由于化工高盐高 COD污水的可生化性极弱,高盐度所造成的高渗透压及高浓度氯离子一定程度上都会对大多 数微生物的存活、生长、繁殖产生严重影响。普通微生物的酶活性在含盐较高的环境,其酶 活受到抑制;因此,在活性污泥中筛选出对高盐环境耐受的菌株成为关键。Usually, the high-salt sewage has a relatively high salt content, >1%, and some are as high as 10%, and because the biodegradability of chemical high-salt and high-COD sewage is extremely weak, the high osmotic pressure and high salinity caused by high salinity The concentration of chloride ions will have a serious impact on the survival, growth and reproduction of most microorganisms to a certain extent. The enzymatic activity of common microorganisms is inhibited in a high-salt environment; therefore, it is key to screen out strains that are tolerant to high-salt environments in activated sludge.

发明内容Contents of the invention

本发明所要解决的技术问题是处理高盐高COD污水中的微生物高盐耐受性较差的问题。The technical problem to be solved by the invention is to deal with the problem that microorganisms in high-salt and high-COD sewage have poor high-salt tolerance.

本发明解决其技术问题所采用的技术方案是:一株耐盐扣囊复膜孢酵母(Saccharomycopsis fibuligera),所述扣囊复膜孢酵母保藏编号为GDMCC No:61874。保藏于 广东微生物菌种保藏中心,保藏日期2021年8月18日,地址:广东省广州市越秀区先烈中路100号大院实验大楼59号楼5楼。The technical solution adopted by the present invention to solve the technical problem is: a strain of salt-tolerant Saccharomycopsis fibuligera, the preservation number of which is GDMCC No: 61874. Preserved in the Guangdong Microbial Culture Collection Center, the preservation date is August 18, 2021, and the address is: 5th Floor, Building 59, Compound Experimental Building, No. 100 Xianlie Middle Road, Yuexiu District, Guangzhou City, Guangdong Province.

其中,上述扣囊复膜孢酵母具有如SEQ ID NO:1所示的核苷酸序列。Wherein, the above-mentioned Saccharomyces spp. has the nucleotide sequence shown in SEQ ID NO:1.

SEQ ID NO:1扣囊复膜孢酵母核苷酸18S rDNA序列1333bp如下:SEQ ID NO: 1 The nucleotide 18S rDNA sequence 1333bp of Saccharomyces forticulata is as follows:

ccgatagtcc ctctaagaag taactatatc agcaaacgct aacagtacta tttagtaggt 60ccgatagtcc ctctaagaag taactatatc agcaaacgct aacagtacta tttagtaggt 60

taaggtctcg ttcgttatcg caattaagca gacaaatcac tccaccaact aagaacggcc 120taaggtctcg ttcgttatcg caattaagca gacaaatcac tccaccaact aagaacggcc 120

atgcaccacc acccacaaaa tcaagaaaga gctctcaatc tgtcaatcct tattgtgtct 180atgcaccacc accccacaaaa tcaagaaaga gctctcaatc tgtcaatcct tattgtgtct 180

ggacctggtg agtttccccg tgttgagtca aattaagccg caggctccac tcctggtggt 240ggacctggtg agtttccccg tgttgagtca aattaagccg caggctccac tcctggtggt 240

gcccttccgt caattccttt aagtttcagc cttgcgacca tactcccccc agaacccaaa 300gcccttccgt caattccttt aagtttcagc cttgcgacca tactcccccc agaacccaaa 300

aactttgatt tctcgtaagg tgccgagtga gtcagtaaaa gaacaacacc cgatccctag 360aactttgatt tctcgtaagg tgccgagtga gtcagtaaaa gaacaacacc cgatccctag 360

tcggcatagt ttatggttaa gactacgacg gtatctgatc atcttcgatc ccctaacttt 420tcggcatagt ttatggttaa gactacgacg gtatctgatc atcttcgatc ccctaacttt 420

cgttcttgat taatgaaaac gtccttggca aatgctttcg cagtagttag tcttcaataa 480cgttcttgat taatgaaaac gtccttggca aatgctttcg cagtagttag tcttcaataa 480

atccaagaat ttcacctctg acaattgaat actgatgccc ccgaccgtcc ctattaatca 540atccaagaat ttcacctctg acaattgaat actgatgccc ccgaccgtcc ctattaatca 540

ttacgatggt cctagaaacc aacaaaatag aaccatacgt cctatttcat tattccatgc 600ttacgatggt cctagaaacc aacaaaatag aaccatacgt cctatttcat tattccatgc 600

taatatattc gagctaaacg cctgctttga acactctaat tttttcaaag taatagtcct 660taatatattc gagctaaacg cctgctttga acactctaat tttttcaaag taatagtcct 660

ggatcatatg cagctgagac aagcccaact acacagaaac caggaggaaa ggctcggctg 720ggatcatatg cagctgagac aagcccaact aacacagaaac caggaggaaa ggctcggctg 720

aaaaccagta ctcgttaaaa aacggaccgg ccagccaagc ccaaagttca actacgagct 780aaaaccagta ctcgttaaaa aacggaccgg ccagccaagc ccaaagttca actacgagct 780

ttttaactgc aacaacttta atatacgctc ttggagctgg aattaccgcg gctgctggca 840ttttaactgc aacaacttta atatacgctc ttggagctgg aattaccgcg gctgctggca 840

ccagacttgc cctccaattg ttcctcgtta aggtatttaa attgtactca ttccaattac 900ccagacttgc cctccaattg ttcctcgtta aggtatttaa attgtactca ttccaattac 900

aagacccgta agggccctgc atcgttatat attgtcacta cctccctgtg tcaggattgg 960aagacccgta agggccctgc atcgttatat attgtcacta cctccctgtg tcaggattgg 960

gtaatttgcg cgcctgctgc cttccttgga tgtggtagcc gtttctcagg ctccctctcc 1020gtaatttgcg cgcctgctgc cttccttgga tgtggtagcc gtttctcagg ctccctctcc 1020

ggaatcgaac ccttattccc cgttacccgt tgaaaccatg gtaggccact atcctaccat 1080ggaatcgaac ccttattccc cgttacccgt tgaaaccatg gtaggccact atcctaccat 1080

cgaaagttga tagggcagaa atttgaatga accatcgcca gcatgaagcc ttgcgattcg 1140cgaaagttga tagggcagaa atttgaatga accatcgcca gcatgaagcc ttgcgattcg 1140

agaagttatt atgaatcacc aaagagcacc gaagtgcatt ggttttttat ctaataaata 1200agaagttat atgaatcacc aaagagcacc gaagtgcatt ggttttttat ctaataaata 1200

catcccttcc aaacagtcgg gatttttagc atgtattagc tctagaatta ccacggttat 1260catcccttcc aaacagtcgg gatttttagc atgtattagc tctagaatta ccacggttat 1260

ccaagtagta aaggtactat caaataaacg ataactgatt taatgagcca ttcgcagttt 1320ccaagtagta aaggtactat caaataaacg ataactgatt taatgagcca ttcgcagttt 1320

cactgtataa ttg                                                    1333cactgtataa ttg 1333

其中,上述扣囊复膜孢酵母的菌株形态特征为灰白状,表面粗糙,菌落边缘不齐,呈放 射状丝状。Wherein, the morphological characteristics of the strain of the above-mentioned Saccharomyces fornicosa yeast are off-white, with a rough surface, irregular colony edges, and radial filaments.

其中,上述扣囊复膜孢酵母在光学显微镜下的个体形态为:丝状、宽2.8-6.09um,有横 梗,膨结。Wherein, the individual shape of the above-mentioned yeast S. fornicata under the optical microscope is: filamentous, 2.8-6.09um wide, with transverse stems and bulging knots.

其中,上述扣囊复膜孢酵母耐受的高盐范围(以NaCl质量计)为30-150g/L。Wherein, the high-salt range (calculated by NaCl mass) tolerated by the above-mentioned Saccharomyces fornicosa yeast is 30-150 g/L.

其中,上述扣囊复膜孢酵母耐受的高盐范围为30-50g/L。Wherein, the range of high salt tolerated by the above-mentioned Saccharomyces fornicosa yeast is 30-50 g/L.

其中,上述扣囊复膜孢酵母耐受高COD范围为15000-17000mg/L。Wherein, the high COD tolerance range of the above-mentioned yeast S. forticulata is 15000-17000 mg/L.

本发明还提供上述任一项所述的耐盐扣囊复膜孢酵母在高盐高COD污水处理中的应用。The present invention also provides the application of the salt-tolerant yeast S. forticulata in the treatment of high-salt and high-COD sewage.

本发明的有益效果是:本发明提供的扣囊复膜孢酵母菌株盐度耐受范围为0%-20%,并 能够在3-5%NaCl,初始COD不低于15000mg/L的条件下进行该COD的降解,通过连续检 测,发现其出水可达可达《污水综合排放标准》GB8978-1996三级。该菌株XW-1具有极高 的盐度耐受能力且在高盐环境下去除COD,因此该菌株在耐盐机理和工业应用上具有潜在的 研究和应用价值。The beneficial effects of the present invention are: the salinity tolerance range of the Saccharomyces spp. provided by the present invention is 0%-20%, and it can be used under the conditions of 3-5% NaCl and an initial COD of not less than 15000mg/L. Carry out the degradation of this COD, through continuous detection, find that its effluent can reach the third grade of "Comprehensive Wastewater Discharge Standard" GB8978-1996. The strain XW-1 has extremely high salinity tolerance and can remove COD in a high-salt environment, so this strain has potential research and application value in the salt tolerance mechanism and industrial application.

本发明提供的扣囊复膜孢酵母菌株于2021年8月18日保藏于广东微生物菌种保藏中心 GDMCC,保藏编号为GDMCC No:61874,生物学分类命名为扣囊复膜孢酵母Saccharomycopsis fibuligera。The yeast strain of Saccharomycopsis fibuligera provided by the present invention was preserved in Guangdong Microorganism Culture Collection Center GDMCC on August 18, 2021, the preservation number is GDMCC No: 61874, and the biological classification is named Saccharomycopsis fibuligera.

附图说明Description of drawings

图1为本发明耐盐扣囊复膜孢酵母菌株菌落形态特征。Fig. 1 is the colony morphological characteristics of the salt-tolerant yeast S. forticulata of the present invention.

图2为本发明耐盐扣囊复膜孢酵母菌株个体形态特征。Fig. 2 is the individual morphological characteristics of the salt-tolerant S. forticulata strain of the present invention.

图3为本发明耐盐扣囊复膜孢酵母菌株在不同盐浓度下的生长情况。Fig. 3 is the growth situation of the salt-tolerant S. forticulata strain of the present invention under different salt concentrations.

图4为本发明耐盐扣囊复膜孢酵母菌株在盐浓度为30g/L对COD的去除效果。Fig. 4 shows the COD removal effect of the salt-tolerant yeast strain of S. forticulata of the present invention at a salt concentration of 30 g/L.

图5为本发明耐盐扣囊复膜孢酵母菌株在盐浓度为50g/L对COD的去除效果。Fig. 5 shows the COD removal effect of the salt-tolerant yeast strain of S. forticulata of the present invention at a salt concentration of 50 g/L.

具体实施方式Detailed ways

下面结合附图和实施例对本发明进一步说明。The present invention will be further described below in conjunction with the accompanying drawings and embodiments.

本发明提供了一株耐盐扣囊复膜孢酵母(Saccharomycopsis fibuligera),保藏编号为 GDMCC No:61874。保藏于广东微生物菌种保藏中心,保藏日期2021年8月16日,地址: 广东省广州市越秀区先烈中路100号大院实验大楼5楼。The invention provides a strain of salt-tolerant Saccharomycopsis fibuligera, the preservation number of which is GDMCC No: 61874. Preserved in the Guangdong Microbial Culture Collection Center, the preservation date is August 16, 2021, and the address is: 5th Floor, Compound Experimental Building, No. 100 Xianlie Middle Road, Yuexiu District, Guangzhou City, Guangdong Province.

上述耐盐扣囊复膜孢酵母菌株分离自泸州老窖酒糟,在PDA平板上其菌株形态特征为: 灰白状,表面粗糙,菌落边缘不齐,呈放射状丝状;在光学显微镜下的个体形态为:丝状、 宽2.8-6.09um,有横梗,膨结;菌株号为XW-1;具有如SEQ ID NO:1所示的核苷酸序列。The above-mentioned salt-tolerant yeast strain of S. forticulata is isolated from Luzhou Laojiao distiller's grains. The morphological characteristics of the strain on the PDA plate are: off-white, rough surface, irregular colony edges, and radial filaments; individual morphology under the optical microscope It is: filamentous, 2.8-6.09um wide, with horizontal stems and swollen knots; the strain number is XW-1; it has the nucleotide sequence shown in SEQ ID NO:1.

本发明扣囊复膜孢酵母耐受的高盐范围为30-150g/L,优选实施盐浓度为30-50g/L,受 高COD范围为15000-17000mg/L。The tolerant high salt range of the present invention is 30-150g/L, and the preferred implementation salt concentration is 30-50g/L, and the high COD range is 15000-17000mg/L.

本发明还提供上述耐盐扣囊复膜孢酵母在高盐高COD污水处理中的应用。The present invention also provides the application of the above-mentioned salt-tolerant yeast S. forticulata in the treatment of high-salt and high-COD sewage.

下面将通过实施例对本发明的具体实施方式做进一步的解释说明,但不表示将本发明的 保护范围限制在实施例所述范围内。The specific embodiment of the present invention will be further explained below by the examples, but it does not mean that protection scope of the present invention is limited in the scope described in the examples.

实施例1 本发明菌株的分离鉴定Embodiment 1 Isolation and identification of bacterial strains of the present invention

取泸州老窖酒糟10g,加入含90mL无菌水的锥形中,30℃120r/min振荡30min后,按10倍梯度稀释,分别取稀释倍数为10-1、10-2、10-3的菌悬液0.1mL涂布于含10%NaCl 的PDA平板,28℃培养,5-7d。将平板上长出的菌落重新采用稀释涂布法分离纯化,直至 得到纯培养物,命名为XW1,于30%的甘油管,-80℃、保藏。菌株XW1的菌落形态特征如 图1,个体形态特征如图2。Take 10g of Luzhou Laojiao distiller's grains, add them into a cone containing 90mL of sterile water, shake at 120r/min at 30°C for 30min, and then dilute in a 10 -fold gradient. Spread 0.1 mL of the bacterial suspension on a PDA plate containing 10% NaCl and incubate at 28°C for 5-7 days. The colony grown on the plate was isolated and purified again by the dilution coating method until a pure culture was obtained, named XW1, and stored in a 30% glycerol tube at -80°C. The colony morphological characteristics of strain XW1 are shown in Figure 1, and the individual morphological characteristics are shown in Figure 2.

实施例2 菌株耐盐生长测定实验Example 2 Determination of Salt-tolerant Growth of Bacterial Strains

菌株XW1的盐度耐受性分析,将菌株XW1的菌株分别接种于含质量分数为0%、1%、3%、5%、7%、10%、13%、15%、20%NaCl的LB平板和液体中培养,37℃倒置 培养,24h观察并记录菌落生长情况如表1。将菌株XW1在不同盐浓度条件下,液体的初始 OD600控制一致,72h后,测定OD600生长情况,判定菌株是否能够耐受且生长,如图3 所示。Salinity tolerance analysis of the strain XW1, the strains of the strain XW1 were respectively inoculated in the Cultivate in LB plate and liquid, culture upside down at 37°C, observe and record the colony growth in 24 hours as shown in Table 1. Under different salt concentration conditions, the initial OD600 of the strain XW1 was controlled to be consistent. After 72 hours, the OD600 growth was measured to determine whether the strain could tolerate and grow, as shown in Figure 3.

表1 菌株XW1盐度梯度试验结果Table 1 Salinity gradient test results of strain XW1

序号serial number 盐度梯度salinity gradient 观察结果(5d)Observations (5d) 序号serial number 盐度梯度salinity gradient 观察结果(5d)Observations (5d) 11 00 ++++++++ 11 00 ++++++++ 22 1%1% ++++++++ 22 10%10% ++++++ 33 2%2% ++++++ 33 13%13% ++++ 44 3%3% ++++++ 44 15%15% ++ 55 5%5% ++++++ 55 18%18% ++ 66 7%7% ++++++ 66 20%20% ++ 77 9%9% ++++++ 77 25%25% ++

注:“++++”长得好,“+++”长得较好;“++”长得一般,“+”能长,”-'“不能长。Note: "++++" looks good, "+++" looks good; "++" looks average, "+" can grow, and "-'" can't.

实施例3 高盐高COD污水去除效果实验Example 3 High-salt and high-COD sewage removal effect experiment

(1)湿菌体的制备:将菌株XW1活化培养和发酵培养后得到XW1菌体发酵培养液。(1) Preparation of wet cells: the XW1 cell fermentation broth was obtained after the strain XW1 was activated and fermented.

(2)耐盐COD去除性能的监测:倒入实验室移动床膜生物反应器(Moving BedBiofilm Reactor,MBBR)中,实验室配水进水NH4-N浓度50mg/L,COD浓度15000-17000mg/L,氯化钠浓度30-50mg/L,每天检测指标有pH、NH4-N、NO2-N、NO3-N、TP、TN并定期分 析菌株XW1在MBBR工艺下耐盐COD去除性能。(2) Monitoring of salt-tolerant COD removal performance: Pour into the laboratory moving bed bioreactor (Moving Bed Biofilm Reactor, MBBR), the laboratory distribution water influent NH 4 -N concentration 50mg/L, COD concentration 15000-17000mg/ L, the concentration of sodium chloride is 30-50mg/L, and the daily detection indicators include pH, NH 4 -N, NO 2 -N, NO 3 -N, TP, TN and regularly analyze the salt-tolerant COD removal performance of the strain XW1 under the MBBR process .

(3)投加耐盐菌后,菌株XW1验证试验持续1个月,进水氯化钠从30g/L升至50g/L,实验室MBBR反应罐出水COD浓度基本为600mg/L左右,进水氨氮被降解完全。(3) After adding salt-tolerant bacteria, the verification test of the strain XW1 lasted for one month, the sodium chloride in the influent rose from 30g/L to 50g/L, and the COD concentration in the effluent of the MBBR reaction tank in the laboratory was basically about 600mg/L. Aqueous ammonia nitrogen is completely degraded.

(4)菌株XW1在高盐污水处理中的应用,进水氯化钠浓度为30g/L,初始COD浓度17000mg/L,通过为期18d的检测研究,发现在第13d的出水可达污水排放标准三级;如图 4。(4) The application of strain XW1 in the treatment of high-salt sewage. The concentration of sodium chloride in the influent is 30g/L, and the initial COD concentration is 17000mg/L. After 18 days of detection and research, it is found that the effluent on the 13th day can reach the sewage discharge standard Level three; as shown in Figure 4.

(5)菌株XW1在高盐污水处理中的应用,进水氯化钠浓度为50g/L,初始COD浓度15000mg/L,通过为期20d的检测研究,发现在第18d的出水可达污水排放标准三级;如图 5。(5) The application of strain XW1 in high-salt sewage treatment, the influent sodium chloride concentration is 50g/L, and the initial COD concentration is 15000mg/L. After 20 days of detection and research, it is found that the effluent water can reach the sewage discharge standard on the 18th day Level three; as shown in Figure 5.

对比例comparative example

处理高盐高COD污水和操作条件与实施例3相同,不同之处在于:在处理过程中投加褶 皱假丝酵母(Candida rugosa)。由于盐浓度仍为30-50g/L,出水高COD无变化稍有增高, 考虑褶皱假丝酵母不具备耐盐去除高COD功能,处理效果不佳,运行失败。Treatment of high-salt high-COD sewage and operating conditions are the same as in Example 3, except that Candida rugosa (Candida rugosa) is added during the treatment process. Since the salt concentration is still 30-50g/L, the high COD of the effluent remains unchanged and slightly increases. Considering that Candida rugosa does not have the function of removing high COD with salt tolerance, the treatment effect is not good, and the operation fails.

该菌株XW1的培养条件和生物转化工艺,除了高盐废水,还可应用于其他高盐废水的 处理。通过上述实施例可以看出,本发明与现有技术相比,具有以下优点:The culture conditions and biotransformation process of the strain XW1 can be applied to the treatment of other high-salt wastewater besides high-salt wastewater. As can be seen from the foregoing embodiments, the present invention has the following advantages compared with the prior art:

1、本发明所培养的菌株XW1菌群浓度高,活性好,能够在开放的体系中迅速成为优势 菌,并能够发挥菌株特定功能;1. The bacterial strain XW1 cultivated by the present invention has a high concentration of flora and good activity, can quickly become a dominant bacterium in an open system, and can exert strain-specific functions;

2、菌株XW1的耐高盐特性达15%NaCl以上,具有很强的生活活性和耐受性;2. The high-salt tolerance of the strain XW1 reaches above 15% NaCl, and has strong living activity and tolerance;

3、可在高盐高COD废水中发挥生化处理功能,适用于各种高盐高COD废水处理;3. It can play a biochemical treatment function in high-salt and high-COD wastewater, and is suitable for the treatment of various high-salt and high-COD wastewater;

4、能够耐受COD大于15000mg/L以上条件下生长,与专利CN 111117913 A报道的红平红球菌(Rhodococcus erythropolis)对比,其进水COD最高负荷只有12000mg/L;本发明的真菌菌株XW1其对高浓度COD的耐受性优于红平红球菌。4. It can grow under the condition that COD is greater than 15000mg/L. Compared with the Rhodococcus erythropolis reported in the patent CN 111117913 A, the highest COD load of its influent is only 12000mg/L; the fungal strain XW1 of the present invention is its The tolerance to high concentrations of COD is better than that of Rhodococcus erythropolis.

5、利用本发明培养的菌株XW1可以解决高盐高COD废水《污水综合排放标准》GB8978-1996三级。5. The bacterial strain XW1 cultivated by the present invention can solve the problem of high-salt and high-COD waste water in the third grade of "Comprehensive Wastewater Discharge Standard" GB8978-1996.

序列表sequence listing

<110> 泸州老窖股份有限公司<110> Luzhou Laojiao Co., Ltd.

南京高新工大生物技术研究院有限公司Nanjing High-Tech University Biotechnology Research Institute Co., Ltd.

泸州品创科技有限公司Luzhou Pinchuang Technology Co., Ltd.

<120> 一株耐盐扣囊复膜孢酵母及其在高盐高COD污水处理中的应用<120> A salt-tolerant yeast strain of S. forticulata and its application in the treatment of high-salt and high-COD sewage

<160> 1<160> 1

<170> SIPOSequenceListing 1.0<170> SIPOSequenceListing 1.0

<210> 1<210> 1

<211> 1333<211> 1333

<212> DNA<212>DNA

<213> 人工序列(Artificial Sequence)<213> Artificial Sequence

<400> 1<400> 1

ccgatagtcc ctctaagaag taactatatc agcaaacgct aacagtacta tttagtaggt 60ccgatagtcc ctctaagaag taactatatc agcaaacgct aacagtacta tttagtaggt 60

taaggtctcg ttcgttatcg caattaagca gacaaatcac tccaccaact aagaacggcc 120taaggtctcg ttcgttatcg caattaagca gacaaatcac tccaccaact aagaacggcc 120

atgcaccacc acccacaaaa tcaagaaaga gctctcaatc tgtcaatcct tattgtgtct 180atgcaccacc accccacaaaa tcaagaaaga gctctcaatc tgtcaatcct tattgtgtct 180

ggacctggtg agtttccccg tgttgagtca aattaagccg caggctccac tcctggtggt 240ggacctggtg agtttccccg tgttgagtca aattaagccg caggctccac tcctggtggt 240

gcccttccgt caattccttt aagtttcagc cttgcgacca tactcccccc agaacccaaa 300gcccttccgt caattccttt aagtttcagc cttgcgacca tactcccccc agaacccaaa 300

aactttgatt tctcgtaagg tgccgagtga gtcagtaaaa gaacaacacc cgatccctag 360aactttgatt tctcgtaagg tgccgagtga gtcagtaaaa gaacaacacc cgatccctag 360

tcggcatagt ttatggttaa gactacgacg gtatctgatc atcttcgatc ccctaacttt 420tcggcatagt ttatggttaa gactacgacg gtatctgatc atcttcgatc ccctaacttt 420

cgttcttgat taatgaaaac gtccttggca aatgctttcg cagtagttag tcttcaataa 480cgttcttgat taatgaaaac gtccttggca aatgctttcg cagtagttag tcttcaataa 480

atccaagaat ttcacctctg acaattgaat actgatgccc ccgaccgtcc ctattaatca 540atccaagaat ttcacctctg acaattgaat actgatgccc ccgaccgtcc ctattaatca 540

ttacgatggt cctagaaacc aacaaaatag aaccatacgt cctatttcat tattccatgc 600ttacgatggt cctagaaacc aacaaaatag aaccatacgt cctatttcat tattccatgc 600

taatatattc gagctaaacg cctgctttga acactctaat tttttcaaag taatagtcct 660taatatattc gagctaaacg cctgctttga acactctaat tttttcaaag taatagtcct 660

ggatcatatg cagctgagac aagcccaact acacagaaac caggaggaaa ggctcggctg 720ggatcatatg cagctgagac aagcccaact aacacagaaac caggaggaaa ggctcggctg 720

aaaaccagta ctcgttaaaa aacggaccgg ccagccaagc ccaaagttca actacgagct 780aaaaccagta ctcgttaaaa aacggaccgg ccagccaagc ccaaagttca actacgagct 780

ttttaactgc aacaacttta atatacgctc ttggagctgg aattaccgcg gctgctggca 840ttttaactgc aacaacttta atatacgctc ttggagctgg aattaccgcg gctgctggca 840

ccagacttgc cctccaattg ttcctcgtta aggtatttaa attgtactca ttccaattac 900ccagacttgc cctccaattg ttcctcgtta aggtatttaa attgtactca ttccaattac 900

aagacccgta agggccctgc atcgttatat attgtcacta cctccctgtg tcaggattgg 960aagacccgta agggccctgc atcgttatat attgtcacta cctccctgtg tcaggattgg 960

gtaatttgcg cgcctgctgc cttccttgga tgtggtagcc gtttctcagg ctccctctcc 1020gtaatttgcg cgcctgctgc cttccttgga tgtggtagcc gtttctcagg ctccctctcc 1020

ggaatcgaac ccttattccc cgttacccgt tgaaaccatg gtaggccact atcctaccat 1080ggaatcgaac ccttattccc cgttacccgt tgaaaccatg gtaggccact atcctaccat 1080

cgaaagttga tagggcagaa atttgaatga accatcgcca gcatgaagcc ttgcgattcg 1140cgaaagttga tagggcagaa atttgaatga accatcgcca gcatgaagcc ttgcgattcg 1140

agaagttatt atgaatcacc aaagagcacc gaagtgcatt ggttttttat ctaataaata 1200agaagttat atgaatcacc aaagagcacc gaagtgcatt ggttttttat ctaataaata 1200

catcccttcc aaacagtcgg gatttttagc atgtattagc tctagaatta ccacggttat 1260catcccttcc aaacagtcgg gatttttagc atgtattagc tctagaatta ccacggttat 1260

ccaagtagta aaggtactat caaataaacg ataactgatt taatgagcca ttcgcagttt 1320ccaagtagta aaggtactat caaataaacg ataactgatt taatgagcca ttcgcagttt 1320

cactgtataa ttg 1333cactgtataa ttg 1333

Claims (2)

1. A strain of salt-tolerant Saccharopolyspora fibuligera is characterized in that: the salt-tolerant saccharomyces cerevisiae fibuligera is deposited with GDMCC No. 61874 and preserved in Guangdong collection of microorganisms with the preservation date 2021, 8 and 16 days.
2. The use of the salt-tolerant Saccharomyces cerevisiae of claim 1 for the treatment of wastewater with NaCl concentrations of 30-50g/L and high COD ranges of 15000-17000mg/L.
CN202111215422.7A 2021-10-19 2021-10-19 Salt-tolerant Saccharomycopsis fibuligera and application thereof in high-salt high-COD sewage treatment Active CN113832042B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202111215422.7A CN113832042B (en) 2021-10-19 2021-10-19 Salt-tolerant Saccharomycopsis fibuligera and application thereof in high-salt high-COD sewage treatment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202111215422.7A CN113832042B (en) 2021-10-19 2021-10-19 Salt-tolerant Saccharomycopsis fibuligera and application thereof in high-salt high-COD sewage treatment

Publications (2)

Publication Number Publication Date
CN113832042A CN113832042A (en) 2021-12-24
CN113832042B true CN113832042B (en) 2023-04-18

Family

ID=78965485

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202111215422.7A Active CN113832042B (en) 2021-10-19 2021-10-19 Salt-tolerant Saccharomycopsis fibuligera and application thereof in high-salt high-COD sewage treatment

Country Status (1)

Country Link
CN (1) CN113832042B (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN116083239A (en) * 2022-12-23 2023-05-09 中蓝连海设计研究院有限公司 Preparation method of salt-tolerant yeast extract powder, product and application thereof

Family Cites Families (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101182473A (en) * 2007-11-14 2008-05-21 哈尔滨工业大学 Preparation method of compound yeast for producing single-cell protein from soybean whey wastewater
WO2017129607A1 (en) * 2016-01-26 2017-08-03 Vib Vzw Improvement of salt tolerance in yeast
CN107189952B (en) * 2017-07-04 2019-05-24 中国食品发酵工业研究院有限公司 A kind of saccharomycopsis fibuligera and its application in high temperature Daqu production
CN109385388B (en) * 2018-12-29 2021-09-14 中蓝连海设计研究院有限公司 Halophilic denitrifying bacteria YL5-2 and application thereof
CN113249273B (en) * 2021-06-30 2022-03-08 泸州老窖股份有限公司 Salt-tolerant bacillus subtilis and application thereof in high-salt ammonia nitrogen wastewater treatment

Also Published As

Publication number Publication date
CN113832042A (en) 2021-12-24

Similar Documents

Publication Publication Date Title
CN107400650B (en) Pseudomonas proteorum and application thereof
WO2020147248A1 (en) Bacterium degrading las and/or n and use thereof
CN105132323B (en) One plant of salt tolerant bacillus and its application in high-salt wastewater processing
WO2021077453A1 (en) Pseudomonas stutzeri, composite microbial inoculum prepared using the pseudomonas stutzeri, and use of the composite microbial inoculum
WO2022165897A1 (en) Acinetobacter vivianii, microbial agent thereof and use thereof
CN111909867B (en) A kind of heterotrophic nitrification-aerobic denitrification bacteria and its cultivation method and application
WO2011079827A1 (en) Extreme halophilic bacteria, composite halophilic bacterium microbial agent and uses thereof
CN107201328B (en) A Chromobacterium strain resistant to sulfonamide antibiotics and its application
CN110656057B (en) Heterotrophic nitrification-aerobic denitrification paracoccus strain, seed liquid, preparation method and application thereof
CN105154366A (en) Bacillus cereus capable of degrading phenol and having electrogenesis characteristic and application thereof
CN102757951A (en) Building and papermaking wastewater treatment method of marine double-fungus co-immobilized system
CN107164276B (en) A strain of Pseudomonas aeruginosa resistant to zinc ion toxicity and its application
CN113832042B (en) Salt-tolerant Saccharomycopsis fibuligera and application thereof in high-salt high-COD sewage treatment
CN110499254B (en) Saline-alkali-resistant aspergillus ochraceus strain W1, and microbial inoculum and application thereof
CN114854620B (en) Degradation strain of N-methylpyrrolidone and application thereof
CN104560746B (en) One plant can handle high salinity organic chemical waste water candida tropicalis and application thereof
CN119040157A (en) Salt-resistant acid-resistant candida tropicalis and application thereof in high-salt strong acid organic wastewater treatment
CN104388343B (en) Microbial flora for treating high-salt industrial wastewater
CN113214999B (en) Geotrichum TN42 and application thereof in sewage treatment
CN110218682A (en) One plant of pseudomycete sample bacillus and its application in mud decrement
JP7055304B2 (en) Lactobacillus parafalaginis strain GBW-HB1903 and its applications
CN105154349A (en) Heterotrophic nitrification halotolerant bacterium and application thereof
CN115838634B (en) Aspergillus polymorpha NXY1, mycelial pellets and their application in shale gas produced water treatment
CN114292767B (en) Lake bacillus alkali strain W30, nitrogen-removing bacteria agent and its preparation method and application
CN116904360A (en) A strain of Weizmannella coagulans and its application in degrading industrial wastewater

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant